CN106517720A - Sewage sludge multi-stage coupling plate-and-frame filter-pressing dewatering device based on multi-point sludge feeding and use method of device - Google Patents
Sewage sludge multi-stage coupling plate-and-frame filter-pressing dewatering device based on multi-point sludge feeding and use method of device Download PDFInfo
- Publication number
- CN106517720A CN106517720A CN201611034688.0A CN201611034688A CN106517720A CN 106517720 A CN106517720 A CN 106517720A CN 201611034688 A CN201611034688 A CN 201611034688A CN 106517720 A CN106517720 A CN 106517720A
- Authority
- CN
- China
- Prior art keywords
- plate
- filter press
- mud
- mud inlet
- frame filter
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 83
- 238000000034 method Methods 0.000 title claims abstract description 45
- 239000010801 sewage sludge Substances 0.000 title claims abstract description 20
- 230000008878 coupling Effects 0.000 title claims description 19
- 238000010168 coupling process Methods 0.000 title claims description 19
- 238000005859 coupling reaction Methods 0.000 title claims description 19
- 238000003825 pressing Methods 0.000 title description 2
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims abstract description 52
- 238000002156 mixing Methods 0.000 claims abstract description 41
- 238000011085 pressure filtration Methods 0.000 claims abstract description 32
- 239000000292 calcium oxide Substances 0.000 claims abstract description 26
- 235000012255 calcium oxide Nutrition 0.000 claims abstract description 26
- 230000018044 dehydration Effects 0.000 claims description 45
- 238000006297 dehydration reaction Methods 0.000 claims description 45
- 239000007787 solid Substances 0.000 claims description 20
- 210000003454 tympanic membrane Anatomy 0.000 claims description 16
- 239000007789 gas Substances 0.000 claims description 15
- 238000001914 filtration Methods 0.000 claims description 12
- 239000003814 drug Substances 0.000 claims description 11
- 239000003570 air Substances 0.000 claims description 10
- 230000008569 process Effects 0.000 claims description 10
- 238000007664 blowing Methods 0.000 claims description 6
- 229940079593 drug Drugs 0.000 claims description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 4
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 4
- 238000005260 corrosion Methods 0.000 claims description 4
- 238000003756 stirring Methods 0.000 claims description 3
- 239000001569 carbon dioxide Substances 0.000 claims description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 2
- 238000005056 compaction Methods 0.000 claims description 2
- 230000003116 impacting effect Effects 0.000 claims description 2
- 229910052757 nitrogen Inorganic materials 0.000 claims description 2
- 239000000203 mixture Substances 0.000 claims 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 26
- 238000012360 testing method Methods 0.000 description 12
- 238000005265 energy consumption Methods 0.000 description 8
- 239000010865 sewage Substances 0.000 description 8
- 230000000694 effects Effects 0.000 description 4
- 238000012546 transfer Methods 0.000 description 4
- 210000004262 dental pulp cavity Anatomy 0.000 description 3
- 230000003750 conditioning effect Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 230000009466 transformation Effects 0.000 description 2
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 229920000297 Rayon Polymers 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 229910001424 calcium ion Inorganic materials 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 230000006835 compression Effects 0.000 description 1
- 238000007906 compression Methods 0.000 description 1
- 230000001143 conditioned effect Effects 0.000 description 1
- 239000002274 desiccant Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 230000003031 feeding effect Effects 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 230000010534 mechanism of action Effects 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/122—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D25/00—Filters formed by clamping together several filtering elements or parts of such elements
- B01D25/12—Filter presses, i.e. of the plate or plate and frame type
- B01D25/21—Plate and frame presses
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Mechanical Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Treatment Of Sludge (AREA)
Abstract
一种基于多点进泥的污水污泥多级耦合板框压滤脱水装置及其使用方法,涉及一种板框压滤脱水装置及其使用方法。本发明是为了解决目前板框压滤机脱水效率低的技术问题。本发明是由进泥总管、进泥支管、板框压滤机、螺旋输送机、混合破碎器、生石灰加药管、二级压滤进泥管组成;板框压滤机的滤板上有5个进泥孔;螺旋输送机位于板框压滤机的下方并与混合破碎器连通,二级压滤进泥管分别与混合破碎器和进泥总管连通,生石灰加药管与混合破碎器连通。本装置的使用方法:第一级压滤、混合破碎、第二级压滤。本发明将污泥含水率降至60%以下,泥饼平面方向的含水率差值可降至0.2%以下,泥饼纵向的含水率差值可降至1%以下。
A multi-stage coupled plate-frame filter press dewatering device for sewage sludge based on multi-point mud feeding and a use method thereof, relating to a plate-frame filter press dewaterer and a use method thereof. The invention aims to solve the technical problem of low dewatering efficiency of the current plate and frame filter press. The present invention is made up of main mud inlet pipe, mud inlet branch pipe, plate and frame filter press, screw conveyor, mixing breaker, quicklime dosing pipe, and secondary filter press mud inlet pipe; the filter plate of the plate and frame filter press has 5 mud inlet holes; the screw conveyor is located under the plate-and-frame filter press and communicates with the mixing crusher, the secondary pressure filter inlet pipe is respectively connected with the mixing crusher and mud inlet main pipe, and the quicklime dosing pipe is connected with the mixing crusher connected. The use method of this device: the first stage of pressure filtration, mixing and crushing, and the second stage of pressure filtration. The invention reduces the water content of the sludge to less than 60%, the water content difference in the plane direction of the mud cake can be reduced to less than 0.2%, and the water content difference in the longitudinal direction of the mud cake can be reduced to less than 1%.
Description
技术领域technical field
本发明涉及一种板框压滤脱水装置及其使用方法。The invention relates to a plate and frame filter press dehydration device and a using method thereof.
背景技术Background technique
目前我国在运行的污水处理厂约3000座,设计日处理能力约1.33×108m3/d。剩余污泥是污水处理的副产物,一般湿污泥量约占总污水量体积的0.3%-0.5%。随着我国经济增长,污水处理量日益增加,剩余污泥产量随之急剧增加,2010年达到2.3~3.0亿吨,2011年达到2.5~3.5亿吨,约以每年超过10%的速度增长。剩余污泥具有组分复杂、含水率高、体积大、性质不稳定、极易腐化并产生臭气等特点,如不加以妥善处置极易对土壤、水体和空气造成二次污染。资料显示,我国污泥处理处置费用超过污水厂总运行费用的30%。剩余污泥的处理处置已成为目前急需解决的问题。《国家中长期科学和技术发展规划纲要(2006-2020年)》中明确指出,需要大力强化污泥减量化、资源化利用与安全处置。At present, there are about 3,000 sewage treatment plants in operation in China, and the designed daily treatment capacity is about 1.33×10 8 m 3 /d. Excess sludge is a by-product of sewage treatment, and the amount of wet sludge generally accounts for about 0.3%-0.5% of the total volume of sewage. With the economic growth of our country, the amount of sewage treatment is increasing day by day, and the output of surplus sludge is increasing rapidly, reaching 230-300 million tons in 2010 and 250-350 million tons in 2011, with an annual growth rate of more than 10%. Surplus sludge has the characteristics of complex components, high moisture content, large volume, unstable properties, easy to rot and produce odor, etc. If it is not properly disposed of, it will easily cause secondary pollution to soil, water and air. Statistics show that the cost of sludge treatment and disposal in my country exceeds 30% of the total operating cost of sewage plants. The treatment and disposal of excess sludge has become an urgent problem to be solved. The "National Medium and Long-Term Science and Technology Development Program (2006-2020)" clearly points out that it is necessary to vigorously strengthen sludge reduction, resource utilization and safe disposal.
目前,污泥的最终处置方式主要有卫生填埋、土地利用、污泥堆肥和污泥焚烧等,然而无论哪种污泥处置方式都要先将污泥进行脱水处理,以降低污泥含水率。剩余污泥含水率一般为97%~99%,包括间隙水、毛细(结合)水、吸附水和内部水。较高含水率的污泥为流动液状,不利于运输和处理处置。当污泥含水率由97%~99%降低到94%~96%时,其体积可缩小到原来的1/4。当污泥含水率为80%时,其填埋占地约是污泥含水率为50%的3.2倍。污泥的脱水减容是污泥处理处置中最重要的一个环节,高效率的脱水将使污泥含水率大幅降低,减小污泥体积,这些因素对于减少污泥外运运费、减少污泥填埋场占地及延长其使用寿命、增大污泥焚烧时的热值、降低污泥后期处理处置费用和为进一步的资源化处理提供有利条件具有重要意义。At present, the final disposal methods of sludge mainly include sanitary landfill, land use, sludge composting and sludge incineration, etc. However, no matter what kind of sludge disposal method, the sludge should be dehydrated first to reduce the moisture content of the sludge . The moisture content of the remaining sludge is generally 97% to 99%, including interstitial water, capillary (bound) water, adsorption water and internal water. Sludge with a relatively high water content is in the form of flowing liquid, which is not conducive to transportation and disposal. When the moisture content of the sludge is reduced from 97% to 99% to 94% to 96%, its volume can be reduced to 1/4 of its original size. When the moisture content of the sludge is 80%, the landfill area is about 3.2 times that of the sludge with a moisture content of 50%. The dehydration and volume reduction of sludge is the most important link in sludge treatment and disposal. High-efficiency dehydration will greatly reduce the moisture content of sludge and reduce the volume of sludge. It is of great significance to occupy landfill and prolong its service life, increase the calorific value of sludge incineration, reduce the cost of sludge post-treatment and disposal, and provide favorable conditions for further resource treatment.
目前污泥脱水过程主要采用的是初级调理后脱水的方式。根据污泥性质与脱水方式的不同,脱水后污泥的含水率有较大波动。目前,我国应用较多的脱水方式是机械脱水,常用的机械脱水方法是带式压滤脱水和板框压滤脱水,主要脱除污泥中的自由水,能耗较高,脱水后泥饼含水率大多在70%~80%,泥饼仍具有一定的流动特性,其后续处置难度和成本仍然较高。近年来,已有一些改进的板框压滤脱水方法可将污泥含水率降低至60%~70%,但大多以增加脱水能耗为代价。如需进一步脱除水分,就需要通过干燥、焚烧等手段,能量消耗较高。而且,通过加大能量输入获得脱水后污泥含水率降低不仅消耗过多的能量,也对设备提出较高的强度要求,从而使得能量损耗、材料浪费更大,处理成本更高。然而,常见的污泥最终处置方式均需要先将污泥处理至含水率60%以下,而环境保护部办公厅文件环办[2010]157号文件“关于加强城镇污水处理厂污泥污染防治工作的通知”中也明确指出:“污水处理厂以贮存(即不处理处置)为目的将污泥运出厂界的,必须将污泥脱水至含水率50%以下”。污泥含水率在60%-65%之间时呈粘浆状,水分子被一层胶体包裹,这个区域称之为污泥的“粘胶相区”,是污泥脱水阻力最大的区域。目前污泥脱水技术、设备难以满足我国更高的环境要求,而国内外在脱水过程参数机理、控制、水分分布及相互转化规律、脱水泥饼微观结构变化规律及相应的作用机制等方面的研究不足,限制了污泥脱水效率的提高。因此,如何在现有的设备条件和能耗范围内有效提高污泥脱水效率已成为污泥减量化、无害化及资源化的关键问题,对于改善环境具有重大的现实意义。At present, the sludge dewatering process mainly adopts the method of dehydration after primary conditioning. According to the different properties of sludge and dehydration methods, the moisture content of sludge after dehydration fluctuates greatly. At present, mechanical dehydration is the most widely used dehydration method in my country. Commonly used mechanical dehydration methods are belt filter press dehydration and plate and frame filter press dehydration. They mainly remove free water in sludge, and the energy consumption is high. After dehydration, the mud cake Most of the water content is 70% to 80%, and the mud cake still has certain flow characteristics, and its subsequent disposal is still difficult and costly. In recent years, there have been some improved plate and frame filter press dehydration methods that can reduce the moisture content of sludge to 60% to 70%, but most of them are at the cost of increasing dehydration energy consumption. If it is necessary to further remove moisture, it needs to be dried, incinerated, etc., and the energy consumption is relatively high. Moreover, reducing the moisture content of dewatered sludge by increasing energy input not only consumes too much energy, but also puts forward higher strength requirements for equipment, resulting in greater energy loss, material waste, and higher processing costs. However, the common final disposal methods of sludge need to treat the sludge to a water content below 60%. However, the document Huanban [2010] No. "Notice" also clearly stated: "Where sewage treatment plants transport sludge to the factory for the purpose of storage (that is, no treatment and disposal), the sludge must be dehydrated to a moisture content of less than 50%." When the moisture content of the sludge is between 60% and 65%, it is viscous, and the water molecules are wrapped by a layer of colloid. This area is called the "viscose phase area" of the sludge, and it is the area with the greatest resistance to sludge dehydration. At present, the sludge dehydration technology and equipment are difficult to meet the higher environmental requirements of our country. However, domestic and foreign researches on the dehydration process parameter mechanism, control, water distribution and mutual transformation law, dewatering cake microstructure change law and corresponding mechanism of action, etc. Insufficient, which limits the improvement of sludge dewatering efficiency. Therefore, how to effectively improve the efficiency of sludge dewatering within the scope of existing equipment conditions and energy consumption has become a key issue for sludge reduction, harmlessness and resource utilization, which has great practical significance for improving the environment.
目前污水处理厂污泥脱水工艺中使用的板框压滤机压滤后的泥饼大多在平面方向和纵向上均存在含水率分布不均的现象。污泥在板框压滤过程中,泥饼外层脱水效率较高,易被压缩,而泥饼中心层则脱水效率较低,相较于外层存在滞后。随着压滤过程的进行,当泥饼外层含水率低于一定程度时,外层泥饼会出现板结现象,阻碍泥饼中心层水分的脱除,泥饼中水分进一步脱除所需的压力大幅度增加,致使泥饼中心层含水率较高,水分难以脱除。同时,目前的板框压滤机大多是单点进泥,泥饼平面方向上也存在含水率分布不均现象,与进泥点距离不同的位置的泥饼含水率存在差异。上述现象均会造成压滤脱水传质不均,极大的限制了脱水效率的提高。At present, the plate and frame filter press used in the sludge dewatering process of the sewage treatment plant mostly has uneven water content distribution in the plane direction and the longitudinal direction of the mud cake after filtration. During the plate and frame filter press process of sludge, the outer layer of the mud cake has a higher dehydration efficiency and is easy to be compressed, while the center layer of the mud cake has a lower dehydration efficiency and lags behind that of the outer layer. With the progress of the filter press process, when the moisture content of the outer layer of the mud cake is lower than a certain level, the outer layer of the mud cake will appear hardened, which will hinder the removal of water in the middle layer of the mud cake, and the required time for further removal of water in the mud cake The pressure increased greatly, resulting in a high moisture content in the center layer of the mud cake, making it difficult to remove the moisture. At the same time, most of the current plate and frame filter presses enter the mud at a single point, and there is also an uneven distribution of moisture content in the direction of the mud cake plane, and there are differences in the moisture content of the mud cake at different distances from the mud entry point. All of the above phenomena will cause uneven mass transfer in filter press dehydration, which greatly limits the improvement of dehydration efficiency.
发明内容Contents of the invention
本发明是为了解决目前板框压滤机压滤后的泥饼在平面方向和纵向上存在含水率分布不均,脱水效率低的技术问题,而提供一种基于多点进泥的污水污泥多级耦合板框压滤脱水装置及其使用方法。The present invention aims to solve the technical problems of uneven water content distribution and low dehydration efficiency in the plane direction and longitudinal direction of the mud cake after plate and frame filter press, and provides a kind of sewage sludge based on multi-point mud feeding. A multi-stage coupling plate and frame filter press dehydration device and a use method thereof.
本发明的基于多点进泥的污水污泥多级耦合板框压滤脱水装置是由一级压滤进泥阀1、进泥总管2、进泥支管3、板框压滤机4、螺旋输送机5、混合破碎器6、生石灰加药管7、柱塞泵或固体泵8、二级压滤进泥管9、二级压滤进泥阀10和进泥泵12组成;所述的进泥支管3由5根管组成,5根管互相平行设置,其中4根管的截面位置构成一个正方形的四个顶点,剩余一根管的截面位于这个正方形的几何中心;所述的板框压滤机4的滤板为正方形,上面有5个进泥孔11,其中一个进泥孔11位于滤板的几何中心点,另外四个进泥孔11位于滤板的四个顶点与几何中心点连线的中间点;所述的进泥支管3的5根管与板框压滤机4的滤板上的5个进泥孔11的位置一一对应;The sewage sludge multi-stage coupling plate and frame filter press dewatering device based on multi-point mud feeding of the present invention is composed of a first-stage filter press mud inlet valve 1, a mud inlet main pipe 2, a mud inlet branch pipe 3, a plate and frame filter press 4, and a screw filter press. Conveyor 5, mixing breaker 6, quicklime dosing pipe 7, plunger pump or solid pump 8, secondary pressure filter inlet pipe 9, secondary pressure filter inlet valve 10 and mud inlet pump 12; The mud inlet branch pipe 3 is composed of 5 pipes, and the 5 pipes are arranged parallel to each other. The cross-sectional positions of the four pipes form the four vertices of a square, and the cross-section of the remaining pipe is located at the geometric center of the square; the plate frame The filter plate of the filter press 4 is a square with five mud inlet holes 11, one of which is located at the geometric center point of the filter plate, and the other four mud inlet holes 11 are located at the four vertices and the geometric center of the filter plate. The middle point of the connecting line; the 5 pipes of the mud inlet branch pipe 3 correspond to the positions of the 5 mud inlet holes 11 on the filter plate of the plate and frame filter press 4;
进泥泵12和一级压滤进泥阀1的一端连接,一级压滤进泥阀1的另一端和进泥总管2连接,进泥总管2的另一端分别与进泥支管3的5根管连通,进泥支管3的5根管的另一端与板框压滤机4的滤板上的5个进泥孔11一一对应连通,螺旋输送机5位于板框压滤机4的正下方,螺旋输送机5的出料口与混合破碎器6的进料口连通,混合破碎器6的出料口与二级压滤进泥管9连通,二级压滤进泥管9的另一端连接一个二级压滤进泥阀10,二级压滤进泥阀10的另一端连接在一级压滤进泥阀1和进泥支管3之间的进泥总管2上,二级压滤进泥管9上设置一个柱塞泵或固体泵8,生石灰加药管7的出药口与混合破碎器6的进药口连通。The mud inlet pump 12 is connected to one end of the mud inlet valve 1 of the first-stage filter press, the other end of the mud inlet valve 1 of the first-stage filter press is connected to the mud inlet main pipe 2, and the other end of the mud inlet main pipe 2 is connected to the 5 ends of the mud inlet branch pipe 3 respectively. The root canals are connected, and the other ends of the five pipes of the mud inlet branch pipe 3 communicate with the five mud inlet holes 11 on the filter plate of the plate and frame filter press 4 one by one. The screw conveyor 5 is located at the bottom of the plate and frame filter press 4 Directly below, the discharge port of the screw conveyor 5 is connected with the feed port of the mixing crusher 6, and the discharge port of the mixing crusher 6 is connected with the mud inlet pipe 9 of the secondary filter press, and the mud inlet pipe 9 of the secondary filter press The other end is connected to a secondary pressure filter mud inlet valve 10, and the other end of the secondary pressure filter mud inlet valve 10 is connected to the mud inlet main pipe 2 between the primary filter pressure mud inlet valve 1 and the mud inlet branch pipe 3. A plunger pump or a solid pump 8 is arranged on the mud inlet pipe 9 of the filter press, and the medicine outlet of the quicklime dosing pipe 7 communicates with the medicine inlet of the mixing crusher 6 .
本发明的基于多点进泥的污水污泥多级耦合板框压滤脱水装置的使用方法如下:The method of using the sewage sludge multi-stage coupling plate and frame filter press dehydration device based on multi-point mud feeding of the present invention is as follows:
一、第一级压滤:打开一级压滤进泥阀1,关闭二级压滤进泥阀10,启动进泥泵12,在低压条件下将待处理的污泥依次通过进泥总管2、进泥支管3和板框压滤机4的滤板上的五个进泥孔11输送进板框压滤机4中,当污泥停止进入板框压滤机4时,提高进泥泵12的压力,在高压条件下将待处理的污泥继续输送进板框压滤机4中进行脱水,当板框压滤机4停止排水时,关闭一级压滤进泥阀2和进泥泵12,然后对板框压滤机4的滤板中的隔膜板鼓气进行鼓膜压滤,当压滤后形成的泥饼出现板结现象时停止鼓膜压滤,完成第一级压滤;1. First-stage filter press: open the first-stage filter press mud inlet valve 1, close the second-stage filter press mud inlet valve 10, start the mud inlet pump 12, and pass the sludge to be treated through the mud inlet main pipe 2 in sequence under low pressure conditions , five mud inlet holes 11 on the filter plate of the mud inlet branch pipe 3 and the plate and frame filter press 4 are transported into the plate and frame filter press 4, and when the sludge stops entering the plate and frame filter press 4, the mud inlet pump is raised 12 pressure, the sludge to be treated will continue to be transported into the plate and frame filter press 4 for dehydration under high pressure conditions. Pump 12, and then carry out tympanic membrane pressure filtration to the diaphragm plate in the filter plate of plate-and-frame filter press 4, stop the tympanic membrane pressure filtration when the mud cake formed after the pressure filtration is hardened, and complete the first stage of pressure filtration;
所述的低压条件是进泥压力为0.4MPa~0.8MPa;所述的高压条件是进泥压力为1.0MPa~1.4MPa;所述的鼓膜压滤的压力为1.2MPa~1.6MPa;The low pressure condition is that the mud inlet pressure is 0.4MPa~0.8MPa; the high pressure condition is that the mud inlet pressure is 1.0MPa~1.4MPa; the pressure of the tympanic membrane filter is 1.2MPa~1.6MPa;
二、混合破碎:第一级压滤后,打开板框压滤机4,压滤后形成的泥饼掉落至螺旋输送机5中,并输送至混合破碎器6中,将生石灰通过生石灰加药管7投加至混合破碎器6中与泥饼一同混合破碎至柱塞泵或固体泵8可以使混合破碎后的污泥进入二级压滤进泥管9中为止;生石灰的投加量为0.01g/gSS~0.05g/gSS;2. Mixing and crushing: After the first stage of pressure filtration, the plate and frame filter press 4 is opened, and the mud cake formed after the pressure filtration falls into the screw conveyor 5, and is transported to the mixing crusher 6, and the quicklime is fed through the quicklime The drug pipe 7 is added to the mixing crusher 6 and mixed with the mud cake until the plunger pump or the solid pump 8 can make the mixed and crushed sludge enter the mud pipe 9 of the secondary pressure filter; the dosage of quicklime 0.01g/gSS~0.05g/gSS;
三、第二级压滤:打开二级压滤进泥阀10和柱塞泵或固体泵8,经过混合破碎器6混合破碎后的污泥依次经过二级压滤进泥管9、进泥总管2、进泥支管3和板框压滤机4的滤板上的五个进泥孔11被输送进板框压滤机4中,当污泥停止进入板框压滤机4时,关闭二级压滤进泥阀10和柱塞泵或固体泵8,然后对板框压滤机4的滤板中的隔膜板鼓气进行鼓膜压滤至板框压滤机4停止排水时停止鼓膜压滤,用干燥气体或热气体对板框压滤机4中的泥饼反吹5min去除泥饼表面的水分,即完成脱水过程;所述的鼓膜压滤的压力为1.6MPa~2.0MPa。3. Second-stage filter press: Open the second-stage filter press mud inlet valve 10 and the plunger pump or solid pump 8, and the sludge mixed and crushed by the mixing crusher 6 passes through the second-stage filter press mud inlet pipe 9 and mud inlet in turn. The main pipe 2, the mud inlet branch pipe 3 and the five mud inlet holes 11 on the filter plate of the plate and frame filter press 4 are transported into the plate and frame filter press 4, and when the sludge stops entering the plate and frame filter press 4, close Second stage filter press mud inlet valve 10 and plunger pump or solid pump 8, and then perform tympanic membrane pressure filtration on the diaphragm plate in the filter plate of plate and frame filter press 4 until the plate and frame filter press 4 stops draining. Press filtration, use dry gas or hot gas to blow back the mud cake in the plate and frame filter press 4 for 5 minutes to remove the moisture on the surface of the mud cake, that is to complete the dehydration process; the pressure of the tympanic filter press is 1.6MPa-2.0MPa.
压滤后形成的泥饼出现板结现象是指泥饼的含水率为80%~90%时的状态。The compaction phenomenon of the mud cake formed after the press filtration refers to the state when the water content of the mud cake is 80% to 90%.
在本发明中,在第一级压滤中,多点进泥的方式在低压进泥阶段能够使板框压滤机中进泥更加均匀,提高进泥量和进泥效果;多点进泥的方式在高压进泥压滤阶段能够提高进泥和压滤的均匀性,减少压滤压力和压滤作用在泥饼平面方向上分布和传质不均的现象,进而提高压滤效果;In the present invention, in the first-stage filter press, the way of multi-point mud feeding can make the mud feeding in the plate and frame filter press more uniform in the low-pressure mud feeding stage, and improve the mud feeding amount and mud feeding effect; multi-point mud feeding The method can improve the uniformity of mud feeding and filtration in the stage of high-pressure mud feeding and pressure filtration, reduce the phenomenon of uneven distribution and mass transfer of pressure and filtration in the plane direction of mud cake, and then improve the effect of filtration;
在本发明中,多点进泥的方式在第二级压滤进泥过程中能够使板框压滤机中进泥更加均匀和顺畅,减小进泥堵塞的可能性,提高进泥量和进泥效果。In the present invention, the method of multi-point mud feeding can make the mud feeding in the plate-and-frame filter press more uniform and smooth during the second-stage filter press mud feeding process, reduce the possibility of mud feeding blockage, and increase the amount of mud feeding and Into the mud effect.
本发明通过多点进泥的方式提高脱水作用在泥饼平面方向上的传质效率,减小泥饼含水率在平面方向上含水率分布不均的现象;同时在泥饼纵向方向外层发生板结现象的初始阶段对泥饼进行破碎处理,混匀后进行二级机械挤压脱水,从而避免泥饼外层板结现象对脱水作用在纵向上的传质效率的限制,减小泥饼含水率在纵向方向上的含水率分布不均的现象;本发明的方法有望提高污泥脱水效率,并减少脱水压力及时间,进而降低脱水能耗和成本。The invention improves the mass transfer efficiency of the dehydration in the plane direction of the mud cake through the way of multi-point mud feeding, and reduces the uneven distribution of the water content of the mud cake in the plane direction; In the initial stage of the hardening phenomenon, the mud cake is crushed, and after mixing, it is dehydrated by secondary mechanical extrusion, so as to avoid the limitation of the outer layer of the mud cake on the mass transfer efficiency of dehydration in the longitudinal direction, and reduce the moisture content of the mud cake The uneven distribution of moisture content in the longitudinal direction; the method of the present invention is expected to improve the sludge dehydration efficiency, reduce dehydration pressure and time, and further reduce dehydration energy consumption and cost.
步骤二中生石灰的投加量0.01g/gSS~0.05g/gSS表示每克的干污泥中投加0.01g~0.05g的生石灰。The dosage of quicklime in step 2 is 0.01g/gSS-0.05g/gSS, which means adding 0.01g-0.05g of quicklime per gram of dry sludge.
本发明的生石灰的作用如下:The effect of unslaked lime of the present invention is as follows:
1、生石灰中钙离子作为污泥骨架结构提高污泥絮体形态结构,提高其抗压性;1. Calcium ions in quicklime serve as the skeleton structure of sludge to improve the morphology and structure of sludge flocs and improve their compression resistance;
2、作为干燥剂;2. As a desiccant;
3、碱性条件破坏污泥胞外聚合物,释放束缚水。3. Alkaline conditions destroy sludge extracellular polymers and release bound water.
本发明的优点:Advantages of the present invention:
(1)本发明可有效降低压滤后泥饼含水率和降低压滤能耗(压力和时间),具有良好的污泥脱水效果,可将污泥含水率由97%~98%降至60%以下,在同等能耗条件下可使压滤后泥饼含水率降低3%~10%;(1) The present invention can effectively reduce the water content of the mud cake after the press filtration and reduce the energy consumption (pressure and time) of the press filter, has a good sludge dehydration effect, and can reduce the water content of the sludge from 97% to 98% to 60% % or less, under the same energy consumption conditions, the moisture content of the mud cake after pressing can be reduced by 3% to 10%;
(2)本发明运行简单,操作方便,与现有板框压滤方法相比无需增加大型设备,无需更换现有设备,可在现有板框压滤机的基础上进行修改即可,升级改造成本低,便于在污水处理厂广泛使用;(2) The present invention is simple in operation and convenient in operation. Compared with the existing plate and frame filter press method, there is no need to increase large-scale equipment, and no need to replace existing equipment. It can be modified and upgraded on the basis of the existing plate and frame filter press. The transformation cost is low, and it is easy to be widely used in sewage treatment plants;
(3)本发明可有效降低压滤后泥饼含水率分布不均的现象,泥饼平面方向不同位置的含水率差值可降至0.2%以下,泥饼纵向(即泥饼中心层和泥饼外层)不同位置的含水率差值可降至1%以下。(3) The present invention can effectively reduce the uneven distribution of water content of the mud cake after press filtration, and the water content difference at different positions in the plane direction of the mud cake can be reduced to below 0.2%. Cake outer layer) the difference in moisture content at different positions can be reduced to less than 1%.
附图说明Description of drawings
图1为具体实施方式一中基于多点进泥的污水污泥多级耦合板框压滤脱水装置的示意图;Fig. 1 is a schematic diagram of a multi-stage coupling plate and frame filter press dehydration device for sewage sludge based on multi-point mud feeding in Embodiment 1;
图2为具体实施方式一中板框压滤机4的滤板的截面图;Fig. 2 is the cross-sectional view of the filter plate of the plate and frame filter press 4 in the specific embodiment one;
图3为图1中进泥支管3沿a-a方向的截面图。Fig. 3 is a sectional view along the a-a direction of the mud inlet branch pipe 3 in Fig. 1 .
具体实施方式detailed description
具体实施方式一:见图1、2和3,本实施方式为一种基于多点进泥的污水污泥多级耦合板框压滤脱水装置,具体是由一级压滤进泥阀1、进泥总管2、进泥支管3、板框压滤机4、螺旋输送机5、混合破碎器6、生石灰加药管7、柱塞泵或固体泵8、二级压滤进泥管9、二级压滤进泥阀10和进泥泵12组成;所述的进泥支管3由5根管组成,5根管互相平行设置,其中4根管的截面位置构成一个正方形的四个顶点,剩余一根管的截面位于这个正方形的几何中心;所述的板框压滤机4的滤板为正方形,上面有5个进泥孔11,其中一个进泥孔11位于滤板的几何中心点,另外四个进泥孔11位于滤板的四个顶点与几何中心点连线的中间点;所述的进泥支管3的5根管与板框压滤机4的滤板上的5个进泥孔11的位置一一对应;Specific implementation mode 1: see Figures 1, 2 and 3. This implementation mode is a multi-stage coupling plate and frame filter press dehydration device for sewage sludge based on multi-point mud entry, specifically consisting of a first-stage filter press mud intake valve 1, Mud inlet main pipe 2, mud inlet branch pipe 3, plate and frame filter press 4, screw conveyor 5, mixing crusher 6, quicklime dosing pipe 7, plunger pump or solid pump 8, secondary pressure filter inlet mud pipe 9, The secondary pressure filter mud inlet valve 10 and the mud inlet pump 12 are composed; the mud inlet branch pipe 3 is composed of 5 pipes, and the 5 pipes are arranged parallel to each other, and the cross-sectional positions of the 4 pipes form four vertices of a square. The section of the remaining pipe is located at the geometric center of the square; the filter plate of the plate-and-frame filter press 4 is a square with five mud inlet holes 11, one of which is located at the geometric center of the filter plate , and the other four mud inlet holes 11 are located at the middle points of the four vertices of the filter plate and the geometric center point; The positions of the mud inlet holes 11 are in one-to-one correspondence;
进泥泵12和一级压滤进泥阀1的一端连接,一级压滤进泥阀1的另一端和进泥总管2连接,进泥总管2的另一端分别与进泥支管3的5根管连通,进泥支管3的5根管的另一端与板框压滤机4的滤板上的5个进泥孔11一一对应连通,螺旋输送机5位于板框压滤机4的正下方,螺旋输送机5的出料口与混合破碎器6的进料口连通,混合破碎器6的出料口与二级压滤进泥管9连通,二级压滤进泥管9的另一端连接一个二级压滤进泥阀10,二级压滤进泥阀10的另一端连接在一级压滤进泥阀1和进泥支管3之间的进泥总管2上,二级压滤进泥管9上设置一个柱塞泵或固体泵8,生石灰加药管7的出药口与混合破碎器6的进药口连通。The mud inlet pump 12 is connected to one end of the mud inlet valve 1 of the first-stage filter press, the other end of the mud inlet valve 1 of the first-stage filter press is connected to the mud inlet main pipe 2, and the other end of the mud inlet main pipe 2 is connected to the 5 ends of the mud inlet branch pipe 3 respectively. The root canals are connected, and the other ends of the five pipes of the mud inlet branch pipe 3 communicate with the five mud inlet holes 11 on the filter plate of the plate and frame filter press 4 one by one. The screw conveyor 5 is located at the bottom of the plate and frame filter press 4 Directly below, the discharge port of the screw conveyor 5 is connected with the feed port of the mixing crusher 6, and the discharge port of the mixing crusher 6 is connected with the mud inlet pipe 9 of the secondary filter press, and the mud inlet pipe 9 of the secondary filter press The other end is connected to a secondary pressure filter mud inlet valve 10, and the other end of the secondary pressure filter mud inlet valve 10 is connected to the mud inlet main pipe 2 between the primary filter pressure mud inlet valve 1 and the mud inlet branch pipe 3. A plunger pump or a solid pump 8 is arranged on the mud inlet pipe 9 of the filter press, and the medicine outlet of the quicklime dosing pipe 7 communicates with the medicine inlet of the mixing crusher 6 .
具体实施方式二:本实施方式为具体实施方式一中基于多点进泥的污水污泥多级耦合板框压滤脱水装置的使用方法,见图1、2和3,具体步骤如下:Embodiment 2: This embodiment is the method of using the sewage sludge multi-stage coupling plate and frame filter press dewatering device based on multi-point mud feeding in Embodiment 1, see Figures 1, 2 and 3, and the specific steps are as follows:
一、第一级压滤:打开一级压滤进泥阀1,关闭二级压滤进泥阀10,启动进泥泵12,在低压条件下将待处理的污泥依次通过进泥总管2、进泥支管3和板框压滤机4的滤板上的五个进泥孔11输送进板框压滤机4中,当污泥停止进入板框压滤机4时,提高进泥泵12的压力,在高压条件下将待处理的污泥继续输送进板框压滤机4中进行脱水,当板框压滤机4停止排水时,关闭一级压滤进泥阀2和进泥泵12,然后对板框压滤机4的滤板中的隔膜板鼓气进行鼓膜压滤,当压滤后形成的泥饼出现板结现象时停止鼓膜压滤,完成第一级压滤,第一级压滤后泥饼含水率为80%~90%;1. First-stage filter press: open the first-stage filter press mud inlet valve 1, close the second-stage filter press mud inlet valve 10, start the mud inlet pump 12, and pass the sludge to be treated through the mud inlet main pipe 2 in sequence under low pressure conditions , five mud inlet holes 11 on the filter plate of the mud inlet branch pipe 3 and the plate and frame filter press 4 are transported into the plate and frame filter press 4, and when the sludge stops entering the plate and frame filter press 4, the mud inlet pump is raised 12 pressure, the sludge to be treated will continue to be transported into the plate and frame filter press 4 for dehydration under high pressure conditions. Pump 12, and then perform tympanic membrane pressure filtration on the diaphragm plate in the filter plate of the plate and frame filter press 4, stop the tympanic membrane pressure filtration when the mud cake formed after the pressure filtration is compacted, and complete the first stage of pressure filtration. The moisture content of the mud cake after the first-stage filter press is 80% to 90%;
所述的低压条件是进泥压力为0.4MPa~0.8MPa;所述的高压条件是进泥压力为1.0MPa~1.4MPa;所述的鼓膜压滤的压力为1.2MPa~1.6MPa;The low pressure condition is that the mud inlet pressure is 0.4MPa~0.8MPa; the high pressure condition is that the mud inlet pressure is 1.0MPa~1.4MPa; the pressure of the tympanic membrane filter is 1.2MPa~1.6MPa;
二、混合破碎:第一级压滤后,打开板框压滤机4,压滤后形成的泥饼掉落至螺旋输送机5中,并输送至混合破碎器6中,将生石灰通过生石灰加药管7投加至混合破碎器6中与泥饼一同混合破碎至柱塞泵或固体泵8可以使混合破碎后的污泥进入二级压滤进泥管9中为止;生石灰的投加量为0.01g/gSS~0.05g/gSS;2. Mixing and crushing: After the first stage of pressure filtration, the plate and frame filter press 4 is opened, and the mud cake formed after the pressure filtration falls into the screw conveyor 5, and is transported to the mixing crusher 6, and the quicklime is fed through the quicklime The drug pipe 7 is added to the mixing crusher 6 and mixed with the mud cake until the plunger pump or the solid pump 8 can make the mixed and crushed sludge enter the mud pipe 9 of the secondary pressure filter; the dosage of quicklime 0.01g/gSS~0.05g/gSS;
三、第二级压滤:打开二级压滤进泥阀10和柱塞泵或固体泵8,经过混合破碎器6混合破碎后的污泥依次经过二级压滤进泥管9、进泥总管2、进泥支管3和板框压滤机4的滤板上的五个进泥孔11被输送进板框压滤机4中,当污泥停止进入板框压滤机4时,关闭二级压滤进泥阀10和柱塞泵或固体泵8,然后对板框压滤机4的滤板中的隔膜板鼓气进行鼓膜压滤至板框压滤机4停止排水时停止鼓膜压滤,用干燥气体或热气体对板框压滤机4中的泥饼反吹5min去除泥饼表面的水分,即完成脱水过程;所述的鼓膜压滤的压力为1.6MPa~2.0MPa。3. Second-stage filter press: Open the second-stage filter press mud inlet valve 10 and the plunger pump or solid pump 8, and the sludge mixed and crushed by the mixing crusher 6 passes through the second-stage filter press mud inlet pipe 9 and mud inlet in turn. The main pipe 2, the mud inlet branch pipe 3 and the five mud inlet holes 11 on the filter plate of the plate and frame filter press 4 are transported into the plate and frame filter press 4, and when the sludge stops entering the plate and frame filter press 4, close Second stage filter press mud inlet valve 10 and plunger pump or solid pump 8, and then perform tympanic membrane pressure filtration on the diaphragm plate in the filter plate of plate and frame filter press 4 until the plate and frame filter press 4 stops draining. Press filtration, use dry gas or hot gas to blow back the mud cake in the plate and frame filter press 4 for 5 minutes to remove the moisture on the surface of the mud cake, that is to complete the dehydration process; the pressure of the tympanic filter press is 1.6MPa-2.0MPa.
具体实施方式三:本实施方式与具体实施方式一的不同点是:所述的混合破碎器6的破碎方式为搅拌或冲击。其他与具体实施方式一相同。Embodiment 3: The difference between this embodiment and Embodiment 1 is that the crushing method of the mixing crusher 6 is stirring or impacting. Others are the same as the first embodiment.
具体实施方式四:本实施方式与具体实施方式一的不同点是:所述的滤板包括隔膜板、配板和防腐板。其他与具体实施方式一相同。Embodiment 4: The difference between this embodiment and Embodiment 1 is that the filter plate includes a diaphragm plate, a matching plate and an anti-corrosion plate. Others are the same as the first embodiment.
具体实施方式五:本实施方式与具体实施方式二的不同点是:步骤一所述的鼓气是通过鼓风机或空压机完成的。其他与具体实施方式二相同。Embodiment 5: The difference between this embodiment and Embodiment 2 is that the blowing described in step 1 is completed by a blower or an air compressor. Others are the same as in the second embodiment.
具体实施方式六:本实施方式与具体实施方式二的不同点是:步骤三所述的鼓气是通过鼓风机或空压机完成的。其他与具体实施方式二相同。Embodiment 6: The difference between this embodiment and Embodiment 2 is that the air blowing described in Step 3 is completed by a blower or an air compressor. Others are the same as in the second embodiment.
具体实施方式七:本实施方式与具体实施方式二的不同点是:步骤三中所述的干燥气体或热气体中的气体为空气、二氧化碳或氮气。其他与具体实施方式二相同。Embodiment 7: The difference between this embodiment and Embodiment 2 is that the gas in the dry gas or hot gas in Step 3 is air, carbon dioxide or nitrogen. Others are the same as in the second embodiment.
具体实施方式八:本实施方式与具体实施方式一的不同点是:5个进泥孔11的面积和小于等于板框压滤机4的滤板中进泥孔11所在面的面积的20%,且大于等于板框压滤机4的滤板中进泥孔11所在面的面积的5%。其他与具体实施方式一相同。Embodiment eight: the difference between this embodiment and embodiment one is: the area of 5 mud inlet holes 11 is less than or equal to 20% of the area of the mud inlet hole 11 in the filter plate of the plate and frame filter press 4 , and greater than or equal to 5% of the area of the surface where the mud inlet hole 11 is located in the filter plate of the plate and frame filter press 4 . Others are the same as the first embodiment.
通过以下试验验证本发明的有益效果:Prove the beneficial effect of the present invention by following test:
试验一:见图1、2和3,本试验为一种基于多点进泥的污水污泥多级耦合板框压滤脱水装置,具体是由一级压滤进泥阀1、进泥总管2、进泥支管3、板框压滤机4、螺旋输送机5、混合破碎器6、生石灰加药管7、柱塞泵或固体泵8、二级压滤进泥管9、二级压滤进泥阀10和进泥泵12组成;所述的进泥支管3由5根管组成,5根管互相平行设置,其中4根管的截面位置构成一个正方形的四个顶点,剩余一根管的截面位于这个正方形的几何中心;所述的板框压滤机4的滤板为正方形,上面有5个进泥孔11,其中一个进泥孔11位于滤板的几何中心点,另外四个进泥孔11位于滤板的四个顶点与几何中心点连线的中间点;所述的进泥支管3的5根管与板框压滤机4的滤板上的5个进泥孔11的位置一一对应;5个进泥孔11的面积和等于板框压滤机4的滤板中进泥孔11所在面的面积的10%Test 1: See Figures 1, 2 and 3. This test is a multi-stage coupling plate and frame filter press dehydration device for sewage sludge based on multi-point mud feeding. Specifically, it consists of a first-stage filter press mud inlet valve 1, mud inlet main pipe 2. Mud inlet branch pipe 3. Plate and frame filter press 4. Screw conveyor 5. Mixing crusher 6. Quicklime dosing pipe 7. Plunger pump or solid pump 8. Secondary pressure filter inlet pipe 9. Secondary pressure filter The filter inlet mud valve 10 and the mud inlet pump 12 are composed; the mud inlet branch pipe 3 is composed of 5 pipes, and the 5 pipes are arranged parallel to each other, and the cross-sectional positions of the 4 pipes form four vertices of a square, and the remaining one The section of the pipe is located at the geometric center of the square; the filter plate of the plate-and-frame filter press 4 is a square with five mud inlet holes 11, one of which is located at the geometric center of the filter plate, and the other four A mud inlet hole 11 is located at the middle point of the four vertices of the filter plate and the geometric center point; the 5 pipes of the mud inlet branch pipe 3 and the 5 mud inlet holes on the filter plate of the plate and frame filter press 4 The positions of 11 are in one-to-one correspondence; the sum of the areas of the five mud inlet holes 11 is equal to 10% of the area of the surface where the mud inlet holes 11 are located in the filter plate of the plate and frame filter press 4
进泥泵12和一级压滤进泥阀1的一端连接,一级压滤进泥阀1的另一端和进泥总管2连接,进泥总管2的另一端分别与进泥支管3的5根管连通,进泥支管3的5根管的另一端与板框压滤机4的滤板上的5个进泥孔11一一对应连通,螺旋输送机5位于板框压滤机4的正下方,螺旋输送机5的出料口与混合破碎器6的进料口连通,混合破碎器6的出料口与二级压滤进泥管9连通,二级压滤进泥管9的另一端连接一个二级压滤进泥阀10,二级压滤进泥阀10的另一端连接在一级压滤进泥阀1和进泥支管3之间的进泥总管2上,二级压滤进泥管9上设置一个柱塞泵或固体泵8,生石灰加药管7的出药口与混合破碎器6的进药口连通。The mud inlet pump 12 is connected to one end of the mud inlet valve 1 of the first-stage filter press, the other end of the mud inlet valve 1 of the first-stage filter press is connected to the mud inlet main pipe 2, and the other end of the mud inlet main pipe 2 is connected to the 5 ends of the mud inlet branch pipe 3 respectively. The root canals are connected, and the other ends of the five pipes of the mud inlet branch pipe 3 communicate with the five mud inlet holes 11 on the filter plate of the plate and frame filter press 4 one by one. The screw conveyor 5 is located at the bottom of the plate and frame filter press 4 Directly below, the discharge port of the screw conveyor 5 is connected with the feed port of the mixing crusher 6, and the discharge port of the mixing crusher 6 is connected with the mud inlet pipe 9 of the secondary filter press, and the mud inlet pipe 9 of the secondary filter press The other end is connected to a secondary pressure filter mud inlet valve 10, and the other end of the secondary pressure filter mud inlet valve 10 is connected to the mud inlet main pipe 2 between the primary filter pressure mud inlet valve 1 and the mud inlet branch pipe 3. A plunger pump or a solid pump 8 is arranged on the mud inlet pipe 9 of the filter press, and the medicine outlet of the quicklime dosing pipe 7 communicates with the medicine inlet of the mixing crusher 6 .
本试验的基于多点进泥的污水污泥多级耦合板框压滤脱水装置的使用方法,见图1、2和3,具体步骤如下:The method of using the sewage sludge multi-stage coupling plate and frame filter press dewatering device based on multi-point mud feeding in this test is shown in Figures 1, 2 and 3. The specific steps are as follows:
待处理的污泥先经16h的重力浓缩,浓缩后污泥含水率97.8%,然后投加聚合氯化铝(PAC)调理污泥,PAC投加量为0.06g/gSS。The sludge to be treated is first concentrated by gravity for 16 hours. After concentration, the moisture content of the sludge is 97.8%. Then polyaluminum chloride (PAC) is added to condition the sludge. The dosage of PAC is 0.06g/gSS.
一、第一级压滤:打开一级压滤进泥阀1,关闭二级压滤进泥阀10,启动进泥泵12,在低压条件下将浓缩、调理后待处理的污泥依次通过进泥总管2、进泥支管3和板框压滤机4的滤板上的五个进泥孔11输送进板框压滤机4中,当污泥停止进入板框压滤机4时,提高进泥泵12的压力,在高压条件下将待处理的污泥继续输送进板框压滤机4中进行脱水,当板框压滤机4停止排水时,关闭一级压滤进泥阀2和进泥泵12,然后对板框压滤机4的滤板中的隔膜板鼓气进行鼓膜压滤,当压滤后形成的泥饼出现板结现象时停止鼓膜压滤,完成第一级压滤;1. First-stage filter press: open the first-stage filter press mud inlet valve 1, close the second-stage filter press mud inlet valve 10, start the mud inlet pump 12, and pass the concentrated and conditioned sludge to be treated in sequence under low pressure conditions. The mud inlet main pipe 2, the mud inlet branch pipe 3 and the five mud inlet holes 11 on the filter plate of the plate and frame filter press 4 are transported into the plate and frame filter press 4. When the sludge stops entering the plate and frame filter press 4, Increase the pressure of the mud inlet pump 12, and continue to transport the sludge to be treated into the plate and frame filter press 4 for dehydration under high pressure conditions. When the plate and frame filter press 4 stops draining, close the first stage filter press mud inlet valve 2 and the mud inlet pump 12, and then perform tympanic membrane pressure filtration on the diaphragm plate in the filter plate of the plate and frame filter press 4, and stop the tympanic membrane pressure filtration when the mud cake formed after the pressure filtration is hardened, and complete the first stage filter press;
所述的低压条件是进泥压力为0.5MPa;所述的高压条件是进泥压力为1.0MPa;所述的鼓膜压滤的压力为1.2MPa;The described low pressure condition is that the mud inlet pressure is 0.5MPa; the described high pressure condition is that the mud inlet pressure is 1.0MPa; the pressure of the tympanic membrane filter press is 1.2MPa;
经第一级压滤后泥饼平均含水率为81.6%,其中泥饼中心层含水率为83.5%,泥饼外层含水率为79.7%;The average moisture content of the mud cake after the first stage of pressure filtration is 81.6%, of which the moisture content of the central layer of the mud cake is 83.5%, and the moisture content of the outer layer of the mud cake is 79.7%;
二、混合破碎:第一级压滤后,打开板框压滤机4,压滤后形成的泥饼掉落至螺旋输送机5中,并输送至混合破碎器6中,将生石灰通过生石灰加药管7投加至混合破碎器6中与泥饼一同混合破碎至柱塞泵或固体泵8可以使混合破碎后的污泥进入二级压滤进泥管9中为止;生石灰的投加量为0.01g/gSS;2. Mixing and crushing: After the first stage of pressure filtration, the plate and frame filter press 4 is opened, and the mud cake formed after the pressure filtration falls into the screw conveyor 5, and is transported to the mixing crusher 6, and the quicklime is fed through the quicklime The drug pipe 7 is added to the mixing crusher 6 and mixed with the mud cake until the plunger pump or the solid pump 8 can make the mixed and crushed sludge enter the mud pipe 9 of the secondary pressure filter; the dosage of quicklime 0.01g/gSS;
三、第二级压滤:打开二级压滤进泥阀10和柱塞泵或固体泵8,经过混合破碎器6混合破碎后的污泥依次经过二级压滤进泥管9、进泥总管2、进泥支管3和板框压滤机4的滤板上的五个进泥孔11被输送进板框压滤机4中,当污泥停止进入板框压滤机4时,关闭二级压滤进泥阀10和柱塞泵或固体泵8,然后对板框压滤机4的滤板中的隔膜板鼓气进行鼓膜压滤至板框压滤机4停止排水时停止鼓膜压滤,用干燥气体对板框压滤机4中的泥饼反吹5min去除泥饼表面的水分,即完成脱水过程;所述的鼓膜压滤的压力为1.6MP。3. Second-stage filter press: Open the second-stage filter press mud inlet valve 10 and the plunger pump or solid pump 8, and the sludge mixed and crushed by the mixing crusher 6 passes through the second-stage filter press mud inlet pipe 9 and mud inlet in turn. The main pipe 2, the mud inlet branch pipe 3 and the five mud inlet holes 11 on the filter plate of the plate and frame filter press 4 are transported into the plate and frame filter press 4, and when the sludge stops entering the plate and frame filter press 4, close Second stage filter press mud inlet valve 10 and plunger pump or solid pump 8, and then perform tympanic membrane pressure filtration on the diaphragm plate in the filter plate of plate and frame filter press 4 until the plate and frame filter press 4 stops draining. For pressure filtration, the mud cake in the plate and frame filter press 4 is blown back with dry gas for 5 minutes to remove the moisture on the surface of the mud cake, that is, the dehydration process is completed; the pressure of the tympanic filter press is 1.6MP.
所述的混合破碎器6的破碎方式为搅拌;所述的滤板包括隔膜板、配板和防腐板;步骤一所述的鼓气是通过鼓风机完成的;步骤三所述的鼓气是通过鼓风机成的;步骤三中所述的干燥气体中的气体为空气。The crushing method of the mixing breaker 6 is stirring; the filter plate includes a diaphragm plate, a matching plate and an anti-corrosion plate; the blowing described in step 1 is done by a blower; the blowing described in step 3 is done by Air blower; the gas in the drying gas described in step 3 is air.
本试验所采用的板框压滤机的过滤面积1.5m2,滤板数量17块(8块隔膜板7块配板和2块防腐板),滤板尺寸为250mm×250mm,滤板厚度15mm,滤室有效容积12.5L。The filter area of the plate and frame filter press used in this test is 1.5m 2 , the number of filter plates is 17 (8 diaphragm plates, 7 matching plates and 2 anti-corrosion plates), the size of the filter plate is 250mm×250mm, and the thickness of the filter plate is 15mm , The effective volume of the filter chamber is 12.5L.
经本试验脱水后的泥饼平均含水率为55.2%,其中泥饼中心层与泥饼外层(纵向)含水率差值最大为0.8%,泥饼平面方向不同位置含水率差值最大为0.3%。The average moisture content of the mud cake after dehydration in this test is 55.2%, and the maximum moisture content difference between the mud cake center layer and the mud cake outer layer (longitudinal) is 0.8%, and the maximum moisture content difference at different positions in the mud cake plane direction is 0.3 %.
试验二:本试验为对比试验:Test 2: This test is a comparative test:
在相同的规格的板框压滤机上,采用相同的污泥原泥,经过相同的浓缩和调理后,通过中心点单点进泥的方式,采用传统的板框压滤方法对污泥进行压滤,在相同的压滤操作方式、压滤压力和压滤时间条件下,即在0.5MPa条件下低压进泥,在1.0MPa条件下高压进泥压滤,在1.2MPa的条件下一次鼓膜压滤,一次鼓膜压滤后板框压滤机不卸泥,直接在1.6MPa的条件下进行二次鼓膜压滤,压滤后泥饼反吹5min。On the plate and frame filter press of the same specification, the same raw sludge is used, after the same concentration and conditioning, the sludge is pressed by the traditional plate and frame filter press method through the central point single point mud feeding method. Under the same pressure filtration operation mode, pressure and time of filtration, that is, under the condition of 0.5MPa, low-pressure mud feeding, under the condition of 1.0MPa, high-pressure mud feeding and pressure filtration, under the condition of 1.2MPa After the first tympanic filter press, the plate and frame filter press does not unload the mud, and directly performs the second tympanic filter under the condition of 1.6MPa, and the mud cake is blown back for 5 minutes after the filter press.
在试验二的条件下采用传统板框压滤方法对污泥进行脱水得到的泥饼平均含水率为61.7%;Under the conditions of Test 2, the average moisture content of the mud cake obtained by dehydrating the sludge by using the traditional plate-and-frame filter press method was 61.7%;
其中靠近中心进泥点处位置的泥饼中心层含水率为62.4%,靠近中心进泥点处位置的泥饼外层含水率为59.4%,泥饼中心层与泥饼外层(纵向)含水率差值为3%;Among them, the moisture content of the central layer of the mud cake near the central mud entry point is 62.4%, the moisture content of the outer layer of the mud cake near the central mud entry point is 59.4%, and the central layer of the mud cake and the outer layer of the mud cake (longitudinal) contain water The rate difference is 3%;
远离中心进泥点处位置的泥饼中心层含水率为63.7%,远离中心进泥点处位置的泥饼外层含水率为61.3%,泥饼平面方向不同位置含水率差值为2.4%。The moisture content of the central layer of the mud cake far away from the central mud entry point is 63.7%, the moisture content of the outer layer of the mud cake far away from the central mud entry point is 61.3%, and the difference in moisture content between different positions in the mud cake plane direction is 2.4%.
分析可知,相比于试验二中传统的板框压滤法,试验一的采用基于多点进泥的污水污泥多级耦合板框压滤脱水方法在相同操作条件和能耗情况下压滤后泥饼平均含水率降低6.5%,且泥饼表面方向和纵向方向上的含水率分布不均现象大幅度减小。The analysis shows that, compared with the traditional plate and frame filter press method in Test 2, the multi-stage coupled plate and frame filter press dehydration method based on multi-point mud feeding in Test 1 was used under the same operating conditions and energy consumption. The average moisture content of the rear mud cake is reduced by 6.5%, and the uneven distribution of moisture content in the surface direction and longitudinal direction of the mud cake is greatly reduced.
Claims (8)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201611034688.0A CN106517720B (en) | 2016-11-22 | 2016-11-22 | A kind of sewage sludge multi-stage coupling plate and frame filter press dewatering device based on multi-point mud feeding and using method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201611034688.0A CN106517720B (en) | 2016-11-22 | 2016-11-22 | A kind of sewage sludge multi-stage coupling plate and frame filter press dewatering device based on multi-point mud feeding and using method thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN106517720A true CN106517720A (en) | 2017-03-22 |
CN106517720B CN106517720B (en) | 2019-04-26 |
Family
ID=58356171
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201611034688.0A Active CN106517720B (en) | 2016-11-22 | 2016-11-22 | A kind of sewage sludge multi-stage coupling plate and frame filter press dewatering device based on multi-point mud feeding and using method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN106517720B (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107638735A (en) * | 2017-10-13 | 2018-01-30 | 河钢股份有限公司承德分公司 | A kind of method by slurry filtration for filtrate |
CN108503176A (en) * | 2017-04-08 | 2018-09-07 | 浙江威治环保科技有限公司 | Microwave improves dehydration and drying method for sludge treatment |
CN108558163A (en) * | 2017-06-03 | 2018-09-21 | 饶宾期 | Sewage sludge electromagnetic force press-filtering dehydration method |
CN110038328A (en) * | 2019-04-24 | 2019-07-23 | 安徽安纳达钛业股份有限公司 | The on-line maintenance method and its application of sheet frame diaphragm filter press |
CN110170188A (en) * | 2019-02-03 | 2019-08-27 | 华汇生态环境产业有限公司 | A kind of filter press |
CN110523115A (en) * | 2019-08-27 | 2019-12-03 | 太原杰安易科技有限公司 | Filter press discharge device operation control method and system |
CN113788596A (en) * | 2021-09-06 | 2021-12-14 | 天津市博川岩土工程有限公司 | A mud treatment device based on a multi-stage cyclone system |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2016942A (en) * | 1977-11-09 | 1979-10-03 | Kuebler H | A method of and an apparatus for expressing liquid from clarifying sludges |
CN202508968U (en) * | 2012-04-24 | 2012-10-31 | 哈尔滨工业大学水资源国家工程研究中心有限公司 | Multi-stage continuous sludge deep dehydration system |
CN203624419U (en) * | 2013-12-24 | 2014-06-04 | 华新环境工程有限公司 | Sludge cake conveying blocking-preventing device |
CN105967496A (en) * | 2016-07-28 | 2016-09-28 | 中国石油化工股份有限公司 | Pollution-free treatment method of high-salt sludge |
-
2016
- 2016-11-22 CN CN201611034688.0A patent/CN106517720B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB2016942A (en) * | 1977-11-09 | 1979-10-03 | Kuebler H | A method of and an apparatus for expressing liquid from clarifying sludges |
CN202508968U (en) * | 2012-04-24 | 2012-10-31 | 哈尔滨工业大学水资源国家工程研究中心有限公司 | Multi-stage continuous sludge deep dehydration system |
CN203624419U (en) * | 2013-12-24 | 2014-06-04 | 华新环境工程有限公司 | Sludge cake conveying blocking-preventing device |
CN105967496A (en) * | 2016-07-28 | 2016-09-28 | 中国石油化工股份有限公司 | Pollution-free treatment method of high-salt sludge |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108503176A (en) * | 2017-04-08 | 2018-09-07 | 浙江威治环保科技有限公司 | Microwave improves dehydration and drying method for sludge treatment |
CN108503176B (en) * | 2017-04-08 | 2019-11-01 | 浙江威治环保科技有限公司 | Microwave improves dehydration and drying method for sludge treatment |
CN108558163A (en) * | 2017-06-03 | 2018-09-21 | 饶宾期 | Sewage sludge electromagnetic force press-filtering dehydration method |
CN107638735A (en) * | 2017-10-13 | 2018-01-30 | 河钢股份有限公司承德分公司 | A kind of method by slurry filtration for filtrate |
CN107638735B (en) * | 2017-10-13 | 2020-05-22 | 河钢股份有限公司承德分公司 | Method for filtering slurry into filtrate |
CN110170188A (en) * | 2019-02-03 | 2019-08-27 | 华汇生态环境产业有限公司 | A kind of filter press |
CN110038328A (en) * | 2019-04-24 | 2019-07-23 | 安徽安纳达钛业股份有限公司 | The on-line maintenance method and its application of sheet frame diaphragm filter press |
CN110038328B (en) * | 2019-04-24 | 2021-09-24 | 安徽安纳达钛业股份有限公司 | Online maintenance method of plate-frame membrane filter press and application thereof |
CN110523115A (en) * | 2019-08-27 | 2019-12-03 | 太原杰安易科技有限公司 | Filter press discharge device operation control method and system |
CN113788596A (en) * | 2021-09-06 | 2021-12-14 | 天津市博川岩土工程有限公司 | A mud treatment device based on a multi-stage cyclone system |
Also Published As
Publication number | Publication date |
---|---|
CN106517720B (en) | 2019-04-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106517720A (en) | Sewage sludge multi-stage coupling plate-and-frame filter-pressing dewatering device based on multi-point sludge feeding and use method of device | |
WO2016058437A1 (en) | Treatment method for deep dewatering of sludge | |
CN104724898B (en) | A kind of sludge pretreatment technique | |
CN104098239B (en) | sewage sludge treatment method | |
CN108383347B (en) | Sludge strengthening treatment and resource utilization device and method for urban sewage treatment plant | |
CN210048640U (en) | Sludge pyrohydrolysis treatment system | |
CN107285604A (en) | A kind of dense mud consolidated depth dewatering of selective oxidation | |
CN102815848B (en) | Surplus sludge high-efficiency drying technique | |
JP2000354900A (en) | Wastewater sludge dehydrating and drying system | |
CN104529128A (en) | Sludge concentration, desiccation and filter pressing system | |
CN204237694U (en) | A kind of stalk and wood chip realize the equipment of deeply dehydrating sludge | |
KR101887416B1 (en) | De-watering Device of Livestock Excretions and De-watering Method thereof | |
CN102358680A (en) | Dehydration method for papermaking waste water sludge | |
CN215756976U (en) | Sludge deep dehydration processing system | |
CN102161557B (en) | A treatment method for excess sludge | |
CN108249732B (en) | A kind of paper mill sludge conditioning, dehydration, desiccation, incineration treatment technology | |
CN204342638U (en) | A kind of sludge concentration desiccation press filteration system | |
CN104098240B (en) | Sewage sludge treatment plant | |
CN110156299A (en) | A kind of municipal sludge broken wall and brick-making method | |
CN102649618A (en) | Method for treating sewage sludge by wood chips | |
CN215288480U (en) | A system for deep dewatering of sludge using an ultra-high pressure press | |
CN104773939B (en) | For the staged dewatering process of Treatment of Sludge | |
CN116002945A (en) | Sludge heatless drying method | |
CN109264962A (en) | A kind of method for sludge treatment and device | |
CN210237418U (en) | Sludge ecological treatment advanced treatment system |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |